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Journal of Threatened Taxa | www.threatenedtaxa.org | 26 April 2015 | 7(5): 7111–7130 Article Article Human-crocodile conflict and conservation implications of Saltwater Crocodiles Crocodylus porosus (Reptilia:

Crocodylia: Crocodylidae) in Sri Lanka ISSN 0974-7907 (Online) ISSN 0974-7893 (Print) A.A. Thasun Amarasinghe 1, Majintha B. Madawala 2, D.M.S. Suranjan Karunarathna 3, 4 5 6 S. Charlie Manolis , Anslem de Silva & Ralf Sommerlad OPEN ACCESS

1 Research Center for Climate Change, University of Indonesia, Gd. PAU Lt. 8.5, Kampus UI, Depok 16424, Indonesia 2 South Australian Herpetology Group, South Australian Museum, North Terrace, Adelaide, SA 5000, Australia 3 Nature Explorations & Education Team, No. B-1/G-6, De Soysapura Housing Scheme, Moratuwa 10400, Sri Lanka 4 Wildlife Management International, PO Box 530, Karama, NT 0813, Australia 5 No. 15/1, Dolosbage Road, Gampola, Sri Lanka 6 Crocodile Conservation Services Europe, RoedelheimerLandstrasse 42, Frankfurt 60487, Germany 1 [email protected] (corresponding author), 2 [email protected], 3 [email protected], 4 [email protected], 5 [email protected], 6 [email protected]

Abstract: Human-wildlife conflict occurs when human requirements encroach on those of wildlife populations, with potential costs to both humans and wild animals. As top predators in most inland waters, crocodilians are involved in human-wildlife conflicts in many countries. Here we present findings of a 5-year survey on human-crocodile conflict on the island of Sri Lanka and relate the results to improving management practices. We aimed to quantify and understand the causes of human-crocodile conflict in Sri Lanka, and propose solutions to mitigate it. Visual encounter surveys were carried out to estimate the population size of Saltwater Crocodiles. We recorded 778 sightings of Saltwater Crocodiles at 262 of 400 locations surveyed, and estimate the total population to comprise more than 2000 non-hatchlings and to have increased at an average rate of 5% p.a. since 1978. We propose four crocodile vigilance zones within the wet zone and one crocodile vigilance zone within the dry zone of the country. Specific threats to Saltwater Crocodiles identified in crocodile vigilance zones were: habitat destruction and loss; illegal killing and harvesting (17 killings out of fear, ~200 incidents of killing for meat and skins, ~800 eggs annually for consumption); unplanned translocations; and, interaction with urbanization (10 incidents of crocodiles being run over by trains/vehicles and electrocution). Additionally, 33 cases of crocodile attacks on humans were recorded [8 fatal, 25 non- fatal (minor to grievous injuries)] and more than 50 incidents of attacks on farm and pet animals.

Keywords: habitat loss, hunting, road kills, policy and planning, translocation, crocodile vigilance zones

Crocodylus porosus Saltwater Crocodile

NOT DATA NEAR CRITICALLY EXTINCT LEAST VULNERABLE ENDANGERED EXTINCT EVALUATED DEFICIENT CONCERN THREATENED ENDANGERED IN THE WILD NE DD LC NT VU EN CR EW EX

DOI: http://dx.doi.org/10.11609/JoTT.o4159.7111-30

Editor: B.C. Choudhury [Retd.], Wildlife Institute of India, Dehradun, India. Date of publication: 26 April 2015 (online & print)

Manuscript details: Ms # o4159 | Received 26 September 2014 | Final received 26 February 2015 | Finally accepted 27 March 2015

Citation: Amarasinghe, A.A.T., M.B. Madawala, D.M.S.S. Karunarathna, S.C. Manolis, A. de Silva & R. Sommerlad (2015). Human-crocodile conflict and conservation implications of Saltwater Crocodiles Crocodylus porosus (Reptilia: Crocodylia: Crocodylidae) in Sri Lanka. Journal of Threatened Taxa 7(5): 7111–7130; http:// dx.doi.org/10.11609/JoTT.o4159.7111-30

Copyright: © Amarasinghe et al. 2015. Creative Commons Attribution 4.0 International License. JoTT allows unrestricted use of this article in any medium, repro- duction and distribution by providing adequate credit to the authors and the source of publication.

Funding: Self funding of AATA, MBM, and DMSSK

Competing Interest: The authors declare no competing interests.

For Author Details, Author Contributionand

Acknowledgements see end of this article

7111 Human-crocodile conflict in Sri Lanka Amarasinghe et al.

INTRODUCTION without conflict with humans. In reality the species has received “paper protection” (Whitaker 2004), with Human-wildlife conflict is a growing issue worldwide the responsible wildlife authority, the Department (Woodroffe et al. 2005) and crocodilians are one of the of Wildlife Conservation (DWC), handling crocodile major groups involved (Lamarque et al. 2009). Sri Lanka issues without sufficient bio-geographical, taxonomic, is a relatively small island of approximately 65,500km2, behavioural or ecological understanding of the species. but home to large populations of crocodiles and other Some management measures, such as the translocation large wild animals (e.g., elephants, leopards, sloth of ‘problem’ crocodiles, have ended with critical bears, etc.), as well as humans. The human population arguments, media debates, and dead or disappeared density in Sri Lanka’s biologically richest wet zone crocodiles. (southwest), is one of the highest on earth (Cincotta et This publication aims at quantifying and al. 2000), and is growing more rapidly around protected understanding the causes of HCC in Sri Lanka, and areas (Wittemyer et al. 2008) and in developing coastal proposes solutions to mitigate it. We also provide new cities such as Colombo, Negombo, Galle, Matara, and insights into the social and biological context in which Hambantota. As a result, human-crocodile conflict crocodile conservation and management programs (HCC) is increasing. could operate in Sri Lanka. Two allopatric species of crocodiles occur in Sri Lanka; the Mugger Crocodile, Crocodylus palustris Lesson, 1831, and the Saltwater or Estuarine Crocodile, Crocodylus MATERIALS AND METHODS porosus Schneider, 1801 (Deraniyagala 1939). The Saltwater Crocodile is the largest living reptile on Earth; Between January 2008 and December 2012 we it can grow up to 6–7 m (Webb et al. 1978; Whitaker visited 400 locations within Gampaha, Colombo, & Whitaker 2008; Erickson et al. 2012). Like other Kalutara, Galle and Matara Districts in the ‘wet zone’ of crocodilians it is an opportunistic feeder, using active the country (Image 1), including beaches from Negombo hunting or ‘sit and wait’ strategies (Cooper & Jenkins on the west coast to Matara on the south coast. We 1993), and the frequency of different prey items varies divided specific survey areas in the wet zone into four significantly with habitat and body size (Taylor 1979; regions (Images 2–5). Systematic surveys in the dry Webb & Manolis 1989). Although telemetry studies are zone could not be carried out due to civil unrest, but increasing our knowledge of movement patterns and some sightings of Saltwater Crocodiles were recorded extent of home ranges for Saltwater Crocodiles (e.g., during general visits to some parts of the area. Webb & Messel 1978; Kay 2004; Read et al. 2007; Brien Spotlight and daytime surveys were carried out from et al. 2008; Campbell et al. 2013, 2014; Hanson et al. boats in rivers, lagoons and other large water bodies, 2014), which can assist management efforts, there is still and we supplemented these counts with other personal a paucity of information for most range states for the observations (both day and night) along small streams species, including Sri Lanka. and canals, marshes, and other small water bodies. We Saltwater Crocodiles are distributed in a wide variety approached crocodiles that were sighted, as close as of saline and freshwater habitats, including rivers and possible to confirm the species and to estimate their creeks, coastlines, coastal flood plains, lagoons, swamps, size. All spotlight survey sightings were recorded as river and canal outfalls (e.g., see Webb & Manolis 1989; “eyes only”. Letnic & Connors 2006). Although popularly referred to Each region was surveyed during different time as ‘salties’ in Sri Lanka, a high proportion of the Saltwater periods (January 2008–March 2009; April 2009–June Crocodile population exists in freshwater habitats in the 2010; July 2010–September 2011; and October 2011– western and southern parts of the country (e.g., Nilwala, December 2012). In all, approximately 500 kilometers Bentota, Kelani, Maha Oya; de Silva 2013), including were surveyed during the 5-year period, representing Colombo, the capital (Devapriya 2004; Jayawardene around 75% of the available habitat for Saltwater 2004; Porej 2004; Samarasinghe 2014). Crocodiles. Under Sri Lankan legislation the Saltwater Crocodile We also examined several Saltwater Crocodiles that is listed as ‘endangered’ (MOE 2012). In the 1970s, had been captured by villagers, unknown groups and Whitaker & Whitaker (1977, 1979), urged the Sri wildlife authorities. We photographed color patterns Lankan Government to establish a sanctuary in which on the flanks and tails of these animals, and other Saltwater Crocodiles would be protected and could live characteristics (e.g., body size, amputations) were

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Image 1. Study area showing the habitat and human population density noted for future identification. These crocodiles were parks. After translocation, we attempted to ascertain translocated by the wildlife authorities to national the fate of the animals through direct observation

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Image 2. Map of Matara–Malimbada–Akuressa Crocodile Vigilance Zone

[e.g. using binoculars (7x50) from jeeps]. Anand et captured and translocated to inland water bodies and to al. (2013) reported that 16 crocodiles (14M: 2F) were Muthurajawela (in Colombo). These animals were not

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Image 3. Map of Beruwala–Benthota–Ambalangoda Crocodile Vigilance Zone responsible for attacks on people, and as we could not our analysis. observe them post-release, they were not included in We interviewed people living around the crocodile

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Image 4. Map of Moratuwa–Dehiwala–Wallawatta Crocodile Vigilance Zone

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Image 5. Map of Ragama–Handala–Wattala Crocodile Vigilance Zone capture locations to identify the extent of HCC. On the zones of high HCC incidence involving Saltwater basis of the survey and interview results we identified Crocodiles within the survey regions, which we refer to

Journal of Threatened Taxa | www.threatenedtaxa.org | 26 April 2015 | 7(5): 7111–7130 7117 Human-crocodile conflict in Sri Lanka Amarasinghe et al. as “Crocodile Vigilance Zones” (CVZ): RHW - Ragama- that juveniles comprise a higher proportion of the Hendala-Wattala; MDW - Moratuwa-Dehiwala- population than is indicated by our results. Hatchlings Wellawatta; BBA - Beruwala-Bentota-Ambalangoda; were sighted in each of the survey regions, but the MMA - Matara-Malimbada-Akuressa. highest numbers were recorded from habitats with well- established vegetation, such as mangroves and riverine forests. RESULTS To derive a total population estimate, we excluded hatchlings and the duplicate counts, applied conservative Crocodile population correction factors of 1.59 to spotlight counts and 2.50 to We recorded 778 sightings of Saltwater Crocodiles daytime counts (Bayliss et al. 1986; Webb et al. 1990), within 262 of the 400 sites visited. The majority of and applied a correction factor of 1.33 to account for sightings were recorded during the day (82.5%), and the habitat that was not surveyed/visited. The current total remainder from spotlight surveys (17.5%). We estimate population is thus estimated to be at least 2000 non- that 25 crocodiles counted during daytime surveys were hatchling Saltwater Crocodiles. Bearing in mind that the re-counted during spotlight surveys, and 98 sightings correction factors that we used to account for sightability were hatchlings (<60cm total length). are conservative, and no attempt was made to correct Most (64%) of the sightings were from the Nilwala for seasonal biases or annual increases in the population River basin (140, 18%); Bentota and Meegama river between 2008 and 2014, this estimate is considered to basins (102, 13%); Dutch-Hamilton Canals and Ja-Ela be an underestimate of the real population size. River (106, 13%); and the Bolgoda River and Lake (154, Interestingly, half of the interviewees who use the 20%). We also observed Saltwater Crocodiles in the water source for daily activities were not aware of the sea or on the seashore at Matara, Beruwala, Bentota, abundance of crocodiles as was observed during the Induruwa, Balapitiya, Kollupitiya, Bambalapitiya, study. Dehiwala, and Ratmalana. A higher proportion of sightings (57%) were recorded from tidal and non-tidal Habitat destruction and loss rivers, than from the coast and freshwater lakes (Fig. 1). The major threats observed for Saltwater Crocodiles On the basis of the daytime surveys, where crocodile in Sri Lanka were: encroachment of human settlements; size estimates were available, juveniles (immature habitat loss and destruction (draining and refilling of non-hatchlings) comprised an estimated 55–60% of wetlands, conversion of mangroves and coastal habitats non-hatchling sightings (see Fig. 2). Given that small for prawn farms, sand extraction, developing tourist crocodiles are not as easily sighted as large crocodiles hotels (including high intensity lighting), unplanned during daytime surveys (Webb et al. 1990), it is likely road/railway constructions); road/rail kills; and, increased fishing activities in the country. In particular, the removal of riverine forests and the reclamation of swamps directly affect Saltwater Crocodile nesting

Figure 2. Size structure of Saltwater Crocodiles sighted in crocodile vigilance zones during 2008–2012. The subadult category comprises mature and immature females Figure 1. Frequency of Saltwater Crocodiles sightings in different and immature males. Eyes Only were recorded during habitats during 2008–2012 spotlight surveys

7118 Journal of Threatened Taxa | www.threatenedtaxa.org | 26 April 2015 | 7(5): 7111–7130 Human-crocodile conflict in Sri Lanka Amarasinghe et al. habits and habitats. Many crocodile habitats are police officers. surrounded by fishing villages and tourism zones, and Most skins were reportedly purchased by ‘foreigners’, the animals in these habitats are potentially impacted usually after being tanned, but a few are in raw salted by motor boat activity, oil, noises, garbage, polythene, form. However, we saw no evidence of products or discarded fishing nets, and fishing tools. We observed handicrafts being manufactured from crocodile skin, higher densities of crocodiles around areas where although such illegal activity may operate covertly. garbage is dumped and which are covered with alien We estimate that over 800 Saltwater Crocodile invasive plants - these habitats may be considered as eggs (equivalent to around 40 nests) were illegally refuge habitats for crocodiles in urban environments. harvested annually for consumption during the 5-year It is possible that crocodiles are attracted to garbage survey period (Fig. 4). Although the full extent of dumps due to the smell of rubbish or other prey items Saltwater Crocodile nesting is unknown at this time, such as rats, birds, dogs, which are attracted to dumped this level of illegal harvest is considered to involve a food. high proportion of nests that are produced. We also observed approximately 20 nests that were predated by Hunting, other killing, and loss of life domestic dogs, Water Monitor Varanus salvator, Land Two-hundred incidents of direct and incidental take Monitor V. bengalensis, Wild Boar Sus scrofa, Jackal of non-hatchling Saltwater Crocodiles were recorded Canis aureus, Python Python molurus, Painted Stork (Fig. 3, Table 1), sometimes as revenge after an attack Mycteria leucocephala and Asian Openbill Anastomus on family members (or friends), but mainly for meat and oscitans, and some cases of cannibalism. skins (Images 6, 7). Juvenile crocodiles (40–120 cm total Nine crocodiles were run over by trains and other length) accounted for 80% of the total take, and most vehicles, and one individual was observed electrocuted (90%) of them were caught incidentally in fishing nets in the Ragama area. (Fig. 3, Image 8) or prawn traps; the remaining 10% were taken as a result of direct hunting. Even the smallest Translocations crocodiles are consumed, after being fried or smoked. Due to the loss of human life, attacks and Crocodile meat is sold in surrounding areas and general increase in HCC, The Department of Wildlife sometimes distributed free amongst neighbours. We Conservation (DWC) started to translocate Saltwater observed crocodile meat being mixed together with Crocodiles from areas of conflict. Most of the suspected and sold as shark meat—one kilogram of crocodile ‘problem’ Saltwater Crocodiles were captured and meat in the Ragama-Handala-Wattala area sold for 300 Sri Lankan Rupees (approximately $US 2.50), whereas shark meat sells for around 900 Rupees (approximately A © M.B. Madawala $US 7.50/kg). While transporting crocodile meat out of an area, hunters use fish containers to hide it from

Capture (to translocate)

Attack on human

Nest har- B © P.D. Weerarathna C © M.B. Madawala vesting

Run over by train/vehicle

Incidental trap

Hunting (meat/skin) Threats to Crocodiles or attacks on humans or attacks Crocodiles to Threats

Kill (fear/ revenge)

0 20 40 60 80 100 Frequency Image 6. A) Saltwater Crocodile killed by villagers in Beruwala on 22 Figure 3. Recorded incidence of threats to Saltwater Crocodiles and December 2011. The animal was injured by two hooks, one in the attacks on humans in crocodile vigilance zones during 2008–2012 stomach (B) and one in the mouth (C)

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Table 1. Saltwater Crocodile killings, road kills and other human-induced mortality recorded in 2008–2013. Hunting, incidental catch and egg collections are not included (CVZ, crocodile vigilance zone - see text for full names; TL, approximate total length of crocodiles)

CVZ Date Location TL Reason for death How the death occurred Responsible for the death

Killing out of fear / considered as a threat / considered as a man-eater Hungangoda - 12 Mar 2008 2.5m Hakmana 10 Jul 2008 Kamburupitiya 2.5m

28 Aug 2009 Nandugala 2m

23 Feb 2010 Vitigala 2.5m Killed by villagers due to Double-sided iron hooks with MMA Malimbada - animal staying around chicken as bait were used 2 Sep 2010 2m Akuressa bathing place. for capture. Cut with an axe Villagers Keerantota - and hit with poles and large 4 Mar 2011 2.5m Akuressa stones. 20 Apr 2011 Kakanadura 2m

17 Mar 2012 Tihagoda 2m Killed by villagers out 15 May 2010 Beruwala 3m of fear. Villagers. After killing the animal, meat divided Munhena - Killed by villagers out Hit with poles and large 18 May 2011 2m amongst villagers to consume. A Beruwala of fear. stones consumed Soft-shell Turtle was observed in the gut. Villagers and DWC. Animal captured on 22 December Attempted to kill by and then informed to DWC, but they Two large single-sided iron villagers out of fear. were late three days. The animal was Beruwala hooks (50 & 75 mm long) 22 Dec 2011 4m People believed that weak and died on the way to the zoo (Fig. 9A) were used (Image 6B-C). Type this crocodile will attack when taking the animal to a surgery of bait unknown. their children to remove the hooks in the mouth BBA and stomach. See footnote (1) for postmortem details. Killed by villagers due to attacks on livestock and Double-sided iron hooks with coming into the kitchen Villagers. After killing the animal the Payagala - chicken bait used for capture. 12 Sep 2012 2.5m of a house. Killed using meat was divided amongst villagers Beruwala Hit with poles and large bait the day after it to consume. stones. was chased back to the waterbody. Killed by villagers as they assumed this Moragalla - Unknown, cut marks on the 2012 - animal was responsible Villagers Beruwala head observed for the death of a male (40 yr) in that area. A large single-sided iron Villagers and DWC. hook (15cm long and 12mm Animal captured at 04.00hr and Killed by villagers as diameter) and double-sided then informed to DWC, who arrived Meda Marsh they assumed this iron hooks (Image 7B) were after 12 hours. [Traveling time from 8 Feb 2012 Dutch Canal 5m animal was responsible used to capture with chicken nearest DWC office (Western Regional (Fig. 10A) for the death of a male bait. Head was cut using an Office, Miriswatta, Gampaha) to (36 yr) in that area. axe and beaten using poles the location, which is around 25km, after approximately 6 hours is approximately 1.5 hours!]. See of capturing. footnote (2) for postmortem details. RHW Double-sided iron hooks with Killed by villagers out of chicken bait used for capture. 22 May 2012 Wanata - Horape 4m fear based on previous Villagers Cut with an axe and hit with experience in Ragama. poles and large stones. Double-sided iron hooks Killed by villagers due to used (specially made to kill Manelgama - 31 Dec 2012 3m attacks on livestock and this crocodile) to capture Villagers Kelaniya a pet dog. with chicken bait. Cut with a machete and hit with poles. Double-sided iron hooks Wewala - Killed by villagers out used to capture with chicken 19 Feb 2009 3m Villagers Piliyandala of fear. bait. Hit with poles and large MDW stones. Hasungala - Killed by a villager out Shot using a 12-gauge single 11 Aug 2012 3m A villager Moratuwa of fear. barrel shotgun.

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CVZ Date Location TL Reason for death How the death occurred Responsible for the death

Run over by trains/vehicles and electrocution Walgama - Apr 2010 2m Matara Guruganga MMA Jul 2011 2.5m Kamburugamuwa Pamburana - Railway development authorities Apr 2012 2m Road kill Run over by train Matara and DWC Madampe - Feb 2008 2m Ambalangoda BBA Jul 2010 Seenigama - Galle 2m Matiwala - Road development authorities and 15 Apr 2010 1.5m Road kill Run over by vehicles Ambalangoda DWC Railway development authorities 19 May 2010 Wattala 2.5m Road kill Run over by train and DWC Improper planning of RHW electricity supply to Electricity board, road development 30 Mar 2013 Mabola 2.5m Electrocution Katunayake-Colombo authorities and DWC Highway project

Feb 2012 Karadiyana - Road development authorities and MDW 1m Road kill Run over vehicles Nov 2012 Piliyandala DWC

Notes: (1) Died on 22 December 2011. Beruwala crocodile (Image 6A) was taken by DWC to surgery for removal of hooks by zoo authorities; the animal was injured by two hooks, one speared the stomach (Image 6B) and other in the mouth (Image 6C), and very bad smell coming from its mouth. The animals died on the way to the zoo before surgery. Polythene, shopping bags, fertilizer bags and bone parts were found in the gut. (2) Died on 8 February 2012. Ragama crocodile (Image 7A) was taken for postmortem by DWC; bleeding at several places on the throat and limbs, head damaged (behind left eye), 10cm deep, 15cm inches wide, cut with an axe (Image 7C), second finger of left foot cut. Seven Black TurtlesMelanochelys trijuga thermalis (Image 7D), ~300g of polythene (Image 7E), ~500g of fertilizer bags, ~2kg of bone parts, five claws of a Fishing Cat Prionailurus viverrinus, and a hand and a leg of a human were found in the gut.

B released into inland freshwater pools which are already © M.B. Madawala heavily populated by Mugger Crocodiles. During the C period of this study DWC released crocodiles to inland © M.B. Madawala pools at Udawalawa, Bundala and Yala National Parks (see Fig. 5, Table 2), and recently to Lunugamwehera National Park (after the study). Field observations since 2000 indicate that Muggers D E and Saltwater Crocodiles do not share the same wild Image 7. A) Saltwater Crocodile that died in Ragama on 8 February habitats, except for a few localities where they may 2012, following capture using double-sided iron hooks (B) and overlap seasonally due to the migration patterns of injuries inflicted to left eye and skull by an axe (C). Seven Black Turtles Melanochelys trijuga thermalis (D) and approximately 300g the latter, which are known to move long distances of polythene (E) were found in the stomach (e.g., Allen 1974; Manolis 2005; Read et al. 2007). For

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Table 2. Translocations of Saltwater Crocodiles in 2008-2013, for which data were recorded and/or were available (CVZ, crocodile vigilance zone - see text for full names; TL, approximate total length of crocodiles; NP, national park; RB, river basin)

CVZ Date Location TL Reason to capture Capturing method Post-release observations Dondra No reason identified, Released to one of the best Mugger habitats in Udawalwa NP. 2010 lighthouse - 3.5m also no record of Unknown Muggers observed chasing it (injured) and disappeared after. Matara harm Most probably dead. Released in Buthawa Wewa Lake (one of the best Mugger Using a steel Malimbada Suspected of killing habitat) in Yala NP. Couldn’t observe after two days, but trackers MMA 15 Feb 2012 4m cage, bait was not (Nilwala RB) school girl (18 yrs.) said that it was seen up until May 2013 in Wilapala Wewa, and confirmed. disappeared after. No reason identified, Matara sea 19 Apr 2012 4.5m also no record of Using ropes Released in Yala NP. Was not observed three days after release. shore harm Released in one of the best Mugger habitats in Udawalwa Kalu Ela Killed chickens and Trap set up by NP. Observed Muggers attacked and injured and no record 23 Feb 2009 5m Hekitta - Wattala pets villagers afterwards. After one week saw a dead body of a huge crocodile RHW (couldn’t confirm identity as carcase had no identifiable marks). Wanata, Ragama Steel cage to Animal captured by an unknown group and believed to be 13 Feb 2012 2m Unidentified group Dutch canal capture released in Yala NP. Accidentally Angulana sea Released in Mugger habitat in Bundala NP. Disappeared three 8 Jan 1999 4m By-catch caught in fishing Moratuwa days after release. net Captured by villagers 17 Jul 2008 Pannipitiya 3m Ropes and cable Released in Mugger habitat in Udawalawa NP. out of fear Using a single- Left limb absent due to a previous incident. Released to Mugger MDW Villagers wanted to 11 Aug 2009 Bolgoda Lake 5.5m sided hook with habitat in Bundala NP. Observed dead body after 3 months. Death kill out of fear chicken bait also confirmed verbally by an officer (anonymous) in Bundala NP. Egodahena, Captured due to 1 Aug 2012 3m Wire mesh cage Released in Lunugamvehera NP (Ratmalana) eating pet dogs Nalluruwa, Trapped in fishing 20 Jan 2013 3m Bycatch Release area unknown Panadura Sea net

Figure 4. Estimated numbers of Saltwater Crocodile eggs illegally harvested annually for consumption in crocodile vigilance zones, together with the numbers of crocodile sightings during 2008–2012 Image 9. Capture of a Saltwater Crocodile by an unknown group on 11 September 2011 at Bolgoda Lake, Hirana, Panadura. (Photo: Anonymous photographer) example, the two species are sympatric during some seasons in the estuary of the Walawe River Basin, and a few localities between Tangalle-Hambantota, Yala as there is a high risk of crocodiles being injured during National Park and Bundala National Park, although the transportation. The types of enclosure being used are latter two localities could reflect introduced populations not appropriate for safe translocation (Image 10), and resulting from translocation activities. their design should consider the health and well-being of The translocation methods used by DWC and the animals (Image 11). In Yala and Udawalawa national unknown groups (Image 9) are considered unacceptable, parks we observed that within a few days, for most of

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Image 10. Saltwater Crocodile captured at Egodahena on 1 August 2012 being transported in cage by wildlife authorities Figure 5. Capture (squares) and translocation (circles) sites for nine Saltwater Crocodiles during 2005–2013

© M.B. Madawala translocations, resident Muggers began to attack the introduced Saltwater Crocodiles, which were always ‘defeated’ and/or injured and tried to move to other pools. Interestingly, half of the observed translocations involved Saltwater Crocodiles estimated to be over 4m in length (Table 2), which may have been considered to be able to deal with Muggers, but this was not the case. As almost all pools are utilized by Muggers, the Saltwater Image 11. Disabled, unhealthy crocodile captured at Bolgoda on 6 Crocodiles had to face the same challenges everywhere, November 2009 and translocated by wildlife authorities ending with fatal injuries or ‘disappearance’ from our visual observations (Table 2). All Mugger translocations carried out by DWC to have been taken by crocodiles. Twenty-five people appeared to be successful, as these animals were were injured during attacks, with injuries ranging from released into Mugger habitats, and we did not observe minor to grievous. Most attacks took place in the early any competition between resident and introduced morning, late evening or at night. Most of the people Muggers. who were attacked were males aged over 30 years, and attacks occurred while victims were bathing or carrying Loss of human life and injuries out activities in water such as washing clothes, washing Since 2008, there were eight confirmed human kitchenware, collecting aquatic plants, and fishing. fatalities caused by Saltwater Crocodile attacks; in addition, three people who ‘disappeared’ are believed

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Hindrance for daily activities most small streams had been ruined. Due to sand mining, The survey indicated that 25% of the people in there has been saltwater intrusion; at times around 5km crocodile habitats enter the water for daily household or more along the river. This phenomenon may result activities and occupations, and were thus vulnerable to in Saltwater Crocodiles swimming upriver, perhaps in attack. Females were attacked while they were washing search of new nesting areas, as most freshwater nesting clothes. Most attacks in the early morning occurred swamps having been now replaced with saline water while people were washing their faces or bathing. Many and other encroachments. As a result, HCC has recently people are afraid to go to the river, and crocodile attacks increased in the upstream Malimbada area, which many have become a common fear in their day-to-day life. crocodiles use for nesting. We observed ideal nesting habitats for Saltwater Crocodile in the Malimbada area, Economic loss which were not found anywhere downstream along the In most of the HCC areas, people are engaged in river, even where there are healthy mangrove habitats. work-related activities associated with water (e.g., Furthermore the lower plains are regularly flooded and fishing, sand mining, farming, plucking aquatic flowers, some crocodiles are able to enter the sea and migrate prawn farming, and illegal alcohol extraction), and from one river basin to another (e.g., on 19 April 2012, so many of them face difficulties to continue their a crocodile ~4.5m long was observed on the Matara jobs, and this directly affects their daily income. In seashore, and on 6 January 2012 a crocodile ~3m long addition, Saltwater Crocodiles have entered small was seen in the sea at Matara). farms run by riverine communities, killing livestock In the Nilwala River, where HCC has increased, we (e.g., chickens, cattle, goats) and pets or guard dogs. As observed many people making small canals towards their Saltwater Crocodiles consume fish (e.g., Oreochromis home gardens to provide water for their cultivations; mossambicus, O. niloticus, Etroplus suratensis, Channa we observed that garbage often blocked these canals, striata, Lates sp.) there is perceived competition for the which contained a well grown aquatic flora, including same food source, and so crocodiles became a common Eichhornia crassipes (Pontederiaceae) [see Fig. 5, plate enemy of fishing communities. 3 in Karunarathna et al. (2010) for similar invasive aquatic plants, in the waterways of Bellanwila-Attidiya Crocodile Vigilance Zones wetland]. This environment makes an ideal habitat and We identified zones of high HCC incidence involving nesting ground for Saltwater Crocodiles. Meat stalls Saltwater Crocodiles, which we refer to as “Crocodile and slaughterhouses pollute the river (e.g., Malimbada Vigilance Zones” (CVZ). We identified five CVZs, four area), as do mini chicken-farms beside the river, of which lie within the wet zone (see Images 2–5) and providing a potential food sources for crocodiles. Many one which we propose for the dry zone. We stress man-eating crocodiles have been killed (using poisoned that there is a risk of increasing HCC within these zones chicken bait) by villagers around the Nilwala River, and and the possibility of it spreading to surrounding areas many unplanned translocations were also conducted in the future unless proper management actions are from this area. implemented. Beruwala-Bentota-Ambalangoda (BBA) Crocodile Matara-Malimbada-Akuressa (MMA) Crocodile Vigilance Zone Vigilance Zone Bentota is a fast developing tourism zone and the The MMA CVZ was identified as having the highest natural vegetation around the Bentota River floodplain rates of killing crocodiles out of fear, road kills, and egg is being replaced with housing, hotels, restaurants, collecting. Matara is a fast developing city and most roads and other tourism activities. Most of the suitable of the natural vegetation around the Nilwala River mangrove habitats and small streams have been floodplains has been replaced with human habitations, replaced with hotels. We observed sea water flowing agriculture, hotels, restaurants, roads and industrial towards the land around 3km along the river, and many units. Most of the suitable habitats had consisted of ideal habitats for Saltwater Crocodiles in the Beruwala mangroves, but now all the small streams have human area have been destroyed. Filling of wetlands, human encroachment. Saltwater Crocodiles generally prefer encroachments, the Beruwala distillery and its water small streams connected to the main river close to pollution, and tourism were identified as growing the sea. We observed some crocodiles digging small threats for Saltwater Crocodiles and their habitats. underground canals across the bank of the river where

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Moratuwa-Dehiwala-Wellawatta (MDW) Crocodile largely unpublished and local news reports. We strongly Vigilance Zone suggest protecting the present mangrove and other The water canals in MDW CVZ are interconnected aquatic vegetation and enriching the habitat. through the city of Colombo to Kalutara and Beruwela in the south, also Kotte marshes, Diyawanna oya, Kirillapone, Wellawatte, Dehiwela and Nedimale canals DISCUSSION to Bellanwila-Attidiya Sanctuary, and then to Bolgoda Lake and then to Kalu River. Furthermore the Mada Ela, Even though Saltwater Crocodiles are afforded starting from Bolgoda Lake, goes as far as Erewwala- legal protection in Sri Lanka, illegal harvesting of eggs Pannipitiya, and is the reason that crocodiles are and hunting (direct and incidental) of crocodiles still recorded from the Pannipitiya area. This zone should occur. The current population estimate of 2000 non- have been the area of highest HCC, but it was not, due hatchlings is considered conservative, and available to the high frequency of crocodile hunting (over 120 data suggest that a high proportion of the population crocodiles were estimated to have been hunted in 2008– comprises immature juveniles, indicative of a recovering 2012) for meat, with most of the meat being sold to population. Despite illegal take of eggs and crocodiles, tourist hotels around Colombo and Moratuwa. Bolgoda the population has increased significantly (at mean rate Lake had provided good habitat for Saltwater Crocodiles, of increase of 5% p.a.) since 1978, when the population but now it is being invaded by human settlements and was estimated to be 375 non-hatchlings (Whitaker & many areas of the wetland have been filled. The riverine Whitaker 1979). Our results confirm that crocodilian vegetation is destroyed and no suitable habitats remain populations have the ability to recover rapidly if harvest for crocodile nesting. That is the reason why crocodiles rates are reduced and/or they are afforded protection, are found in Colombo (on 20 February 2012 a crocodile and habitats (including nesting habitats) remain intact. ~3m long was observed in Colombo Dockyard Sea) and The study also confirmed that habitats are under threat Dehiwala (a ~2m long crocodile was seen in Dehiwala- largely due to an increasing human population, and the Wellawatta canal, and a 2m crocodile was seen on7 impact of illegal harvesting in the future needs to be February 2012 in Rattanapitiya Canal and Moratuwa, addressed. which is interconnected with Bellanwila-Attidiya Both Muggers and Saltwater Crocodiles attack Sanctuary and Bolgoda Lake by canals). humans (e.g., Caldicott et al. 2005), and are responsible for numerous fatalities each year (Somaweera & de Silva Ragama-Hendala-Wattala (RHW) Crocodile Vigilance 2013). Crocodile attacks are common in Sri Lanka, in part Zone because there are high numbers of large crocodiles in This narrow canal system fulfills the requirements for the population (191 crocodiles sighted were >3m long, Saltwater Crocodile habitat similar to the small streams and were most likely males; Webb & Manolis 1989), made by people in MMA CVZ. Most areas of Hamilton but mainly due to the reliance of increasing numbers Canal are well covered with many aquatic floating plants of people on water resources that contain crocodiles. such as E. crassipes. RHW CVZ has a very high number HCC is sometimes attributed to overfishing of one of of meat stalls and slaughterhouses and mini chicken- the crocodile’s main food sources, leading crocodiles to farms. Also humans have encroached to the margin of hunt other prey, including humans (Uragoda 1994; Rao the canal and in some areas invaded the canal as well. 1996; Anderson & Pariela 2005). This competition can Muthurajawela and other marshes in Colombo are take the form of theft of live fish from fishing nets and the main water drainage system, especially during the associated damage to fishing gear, and diminishing the southwest monsoon. daily catch of fishing communities (de Silva 2013). Notwithstanding the bad image that crocodiles Kalmune-Batticaloa-Eravur-Kalkuda (KBEK) Crocodile receive as a result of HCC (Santiapillai et al. 2004), Vigilance Zone our study confirmed previous reports that crocodiles We propose KBEK CVZ, which lies within the dry are opportunistically killed or directly hunted for their zone, as an emerging conflict area, and there is a need meat (Senanayake 1995). Whitaker & Whitaker (1977) for immediate surveys to identify the core issues before mentioned that crocodile meat resembles shark meat in the conflict becomes worse. The crocodile population terms of taste and texture, and is eaten by people for data and movement patterns are not well identified for its purported curative properties (de Silva 2008, 2013). this area, except for a few preliminary surveys that are Attempts by government to mitigate HCC through

Journal of Threatened Taxa | www.threatenedtaxa.org | 26 April 2015 | 7(5): 7111–7130 7125 Human-crocodile conflict in Sri Lanka Amarasinghe et al. the translocation of crocodiles do not appear to have Diverse tourist activities like speed-boats, tourist taken into account the biology of the species, nor has the boat tours and fishing have led to the disappearance effectiveness of this strategy been assessed until now. of crocodiles (Gramentz 2008) in BBA CVZ. According Muggers are mainly concentrated in national parks and to Gramentz (2008), at one location along the Bentota man-made reservoirs in the dry zone (de Silva & Lenin River, 39 boats were involved with sand extraction 2010; de Silva 2013), and according to Santiapillai & de within a 75-minute period. There were no crocodiles Silva (2001) they are sympatric with Saltwater Crocodiles recorded in the sea in front of Bentota River (Gramentz at 25 localities, most of which are uncertain. Previous 2008), and many crocodiles have migrated to adjacent translocations by DWC assumed that the two species healthier habitats, which may explain their occurrence are sympatric, but it appears that these translocations on the seashore of BBA CVZ, and recently in Madu Ganga have modified the natural distributions of both species (De Silva & de Silva 2008). We recommend that speed in Sri Lanka, and resulted in mortality of translocated boats not be permitted to enter at least some parts of Saltwater Crocodiles due to social interactions with Dedduwa Lake (e.g., eastern side of Elpitiya Road Bridge) Muggers. and the upper river. Removal of human encroachments Conservation is an important national and from the buffer zone of the Dedduwa Lake area, and international issue, and it is incumbent upon educators, limiting or restricting of sand mining at least as far as the conservation managers, legal advisors, funding agencies, Udugama area, are important. The banning of fishing officials and policy makers to work along with research nets being stretched right across the river and halting scientists to ensure that inaccurate information does of further permissions for new houses or extensions to not endanger efforts to safeguard Sri Lanka’s remaining those already on the bank, with the implementation of endangered biodiversity treasures (Bahir & Gabadage enforcement measures, are also recommended (see 2009), therefore management should be based on the also Gramentz 2008). best available information. We suggest implementing a proper recycling or disposal plan for the Karadiyana garbage dump in MDW CVZ. In addition, cleaning the canals in Dehiwala, MANAGEMENT IMPLICATIONS OF HUMAN- Wellawatta, Colombo area, the reintroduction of CROCODILE CONFLICT mangroves to Bolgoda Lake, and the removal of unpermitted human encroachments, meat stalls and Habitat enrichment and restoration slaughterhouses from Dehiwala-Wellawatta canal Notwithstanding the issues associated with HCC, the buffer zone is very important and urgent. The current ability of Sri Lanka to maintain healthy wild populations wetland fills and unplanned developments will lead to of Saltwater Crocodiles will ultimately depend on future flooding in Colombo, a similar scenario to that the availability of suitable habitats. Habitat loss and in Jakarta, Indonesia (Caljouw et al. 2005). Devapriya destruction, including human encroachment, are (2004) observed 20 Saltwater Crocodiles along a 2.8- the key factors affecting natural Saltwater Crocodile km stretch of the Dandugam Oya and 2–9 individuals in habitats in Sri Lanka. Habitat restoration, including the 1.7km of adjacent marsh, showing that they move from reintroduction of mangroves on government-owned Negombo Lagoon to adjacent river basins. lands, removal of unpermitted human encroachments The Dutch Canal, commenced in 1802, links the from buffer zones of river and swamp areas and resettling Kelani River with the main seaport of Negombo Lagoon, of people outside of buffer zones, immediate action and was intended to drain the Muthurajawela Marsh. to reduce saltwater intrusion into freshwater bodies, However the effect was the opposite and the high restricting the issuing of new permits for sand mining tides brought in a larger amount of saline water. This near river mouths (at least 10km from the river mouth), created ideal habitats for Saltwater Crocodiles and prohibition on the dumping of garbage and farm refuse, they bred well in these canals. This was the reason and cleaning up garbage and invasive aquatic plants in for the increase in HCC in RHW CVZ associated with man-made streams leading into rivers, are actions that Hamilton Canal. Also this canal network gives access to can be considered within a strategy to improve and Saltwater Crocodiles to the main channel of the Kelani maintain habitat quality in the short- and long-term. As River, a major reason why some have been recorded most CVZs are rapidly developing with emergent plans from Awissawella, over 50 km away inland from RHW for widening roads and new highways (RDA 2007), the CVZ. Removal of unpermitted human encroachments, design of new roads should also be considered. meat stalls and slaughterhouses from Hamilton Canal

7126 Journal of Threatened Taxa | www.threatenedtaxa.org | 26 April 2015 | 7(5): 7111–7130 Human-crocodile conflict in Sri Lanka Amarasinghe et al. and maintaining a buffer zone, stopping the dumping which local communities can facilitate and contribute to garbage and farm refuse into the canal, and cleaning the construction of CEEs merits consideration - it would up garbage and invasive aquatic plants in the canal are not only speed up the implementation of CEEs in areas considered important and urgent actions. of HCC, but give communities a sense of ownership (CSG 2015a). Other initiatives, such as the provision of Awareness water pipelines to rural communities would improve Crocodiles are mostly killed by people out of fear the quality of drinking water, and reduce the reliance of attacks (Senanayake 1995), and has contributed to on people to carry out some activities near/in crocodile the existing bad image that crocodiles have (Santiapillai habitats. et al. 2004). Nowadays, the public’s attitude towards crocodiles is ‘negative’, and crocodiles are simply Translocation regarded as man-eaters, monsters and killers. The The effectiveness of translocation as a suitable importance of public awareness was pointed out over management option for the mitigation of HCC with 35 years ago by Whitaker & Whitaker (1979), when the Saltwater Crocodiles within a Sri Lankan context is frequency of HCC was low. Now HCC has increased, and unclear. Saltwater Crocodiles have a strong homing there is a need at a national level for increased public instinct, and translocation may result in return tothe education and awareness about crocodiles. original capture site (Webb & Manolis 1989; Walsh Effective conservation of Saltwater Crocodiles & Whitehead 1993; Read et al. 2007). In northern will involve a diverse range of stakeholders, including Australia, translocated Saltwater Crocodiles appear to Government agencies, non-government organisations, become more mobile, and two Saltwater Crocodiles business and tourism sectors, the media, the public (rural were subsequently involved in attacks on humans. and urban), etc., each of which may need to be involved Translocation of Saltwater Crocodiles into the wild may with or be the target of a dedicated public education and thus not be an effective strategy for managing HCC, and awareness program. Crocodiles potentially “involve” may indeed exacerbate it. a suite of government jurisdictions other than DWC, We suggest that only ‘problem’ crocodiles which have and so it is important that these other agencies (e.g., been involved in attacks or which pose a real threat to transport, tourism, housing, agriculture, water, fishing, humans and livestock be captured and translocated, and police, military) are aware of crocodile management that this be to captive facilities (see later). Government initiatives and environmental legislation as it pertains to agencies may need to develop guidelines on appropriate crocodiles and other wildlife. Ideally everyone should capture and handling techniques. At an international be rowing in the same direction! level, some countries have implemented Codes of Saltwater Crocodiles are large predators, and Practice that have been applied to both wild and captive humans are well within the size of prey that can be crocodilians (e.g., NRMCC 2009; CFAZ 2012), and which taken. Thus, public education about crocodiles should also take into account animal welfare considerations inform people about the real dangers and realities of (see Image 11). ‘living with crocodiles’, but also convey the reasons why crocodiles need to be conserved. Getting that message National surveys and research projects across to the diverse range of stakeholders in Sri Lanka We suggest that a population monitoring program will no doubt involve a suite of different strategies, be developed to quantify population trends in different ranging from brochures, pamphlets, signage, media parts of the country over time, and to identify further coverage, school curriculum (Beehler 2011), T-shirts, CVZs and threats to crocodiles and people. The calendars, posters, public presentations, tourist guides, frequency of crocodile attacks, size structure of the museum exhibits, etc. To the extent possible, the media population, extent of nesting, etc., could provide should present a balanced view on crocodiles, as it is an additional indices of the population that can help important vehicle to assist public education. guide management. DWC, in collaboration with local Crocodile Exclusion Enclosures (CEE) have been used researchers, is planning a national survey of crocodiles, effectively in Sri Lanka, and have no doubt contributed to and it is greatly appreciated that DWC will initiate such reductions in HCC. However, the significant cost involved ground level research towards proper science-based with the construction and ongoing maintenance of CEEs management. has constrained the Sri Lankan Government’s plans to build more of them (CSG 2015a). A mechanism through

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Ex situ or semi in situ conservation (Crocodile National country is different, and crocodile management in Sri Park) Lanka will need to take into account the economic, A captive or semi-natural reserve could assist social and cultural context of the country. conservation efforts for crocodiles in Sri Lanka, as was As the lead agency for crocodiles in Sri Lanka, suggested in the 1970s by Whitaker & Whitaker (1979). improving DWC’s capacity to deal with HCC and crocodile Such a reserve or facility would not only provide a site management in general, and increasing scientific for release of problem crocodiles captured to reduce capacity (Pethiyagoda et al. 2007; Bahir & Gabadage HCC, but could also serve as a centre of public education, 2009; Amarasinghe et al. 2014) will no doubt assist the training (local and international participants), captive country’s efforts to ensure the long-term conservation breeding, research and recreation (tourism). 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Specialist Group Newsletter 27: 26–30. Author Contribution: AATA, MBM, and DMSSK conceived the concept, ideas, Whitaker, R. & Z. Whitaker (1977). Sri Lanka crocodile survey. Loris plan of work and did field work; AATA prepared the maps and manuscript; 14: 239–241. AdS and RS contributed data and improved the manuscript; CM helped with preparing the manuscript and final editing. Whitaker, R. & Z. Whitaker (1979). Preliminary crocodile survey - Sri Lanka. Journal of Bombay Natural History Society 76: 66–85. Author Details: All the authors are commission members of the Crocodile Wittemyer, G., P. Elsen, W.T. Bean, A.C.O. Burton & J.S. Brashares Specialist Group (CSG), Species Survival Commission (SSC), International Union (2008). Accelerated human population growth at protected area for Conservation of Nature (IUCN). edges. Science 321: 123–126. Woodroffe, R., S. Thirgood & A. Rabinowitz (2005). People and Acknowledgements: We thank Colin Groves, Mohamed Bahir and other Wildlife: Conflict or Coexistence. Cambridge University Press, UK, anonymous reviewers who critically reviewed this manuscript and helped improve the quality; Special acknowledgement to the field survey team for their 516pp. assistance in the field. Then we would like to thank many national park rangers and safari guides, safari jeep drivers in Udawalwa, Yala and Bundala National Parks for providing all the translocation details and help to locate animals inside Threatened Taxa national parks, villagers in study areas for providing information, and safari jeep owners for providing transportation to visit national parks and locate the translocated crocodiles. Finally, we would like to thank members of the Young Zoologists’ Association (YZA) for their support; A. Godahewa, J. Ranasinghe and P.D. Weeraratne for photographs.

7130 Journal of Threatened Taxa | www.threatenedtaxa.org | 26 April 2015 | 7(5): 7111–7130